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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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EC number: - | CAS number: -
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Water solubility
Administrative data
Link to relevant study record(s)
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- July 2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Key result
- Water solubility:
- < 0.051 mg/L
- Conc. based on:
- test mat.
- Loading of aqueous phase:
- 73 mg/L
- Incubation duration:
- 24 h
- Temp.:
- 20 °C
- pH:
- 7
- Details on results:
- As no test item was detected in the majority of the samples, and where test item was detected, the response was significantly below that of the lowest calibration standard, the result has been reported as a limit value. The Iimit value used is the level at which satisfactory recovery was demonstrated for the sample analysis procedure, i.e. 5.06 x 10-5 g/L.
- Conclusions:
According the TG OECD 105 and GLP study, the water solubility of the test material is less than 5.06 x 10-5 g/L of solution at 20.0 ± 0.5 °C.- Executive summary:
An experimental study was performed in accordance with GLP and TG OECD 105 to determine the water solubility of the test item. The solubility is less than 0.0506 mg/L at 20°C, and the substance is therefore considered insoluble in water.
Reference
The preliminary water solubility test indicated that the column elution method should have been performed as the solubility was less than 1x10-2g/L. However, due to the extremely low water solubility of the test item, a large volume of sample was required for the analysis. This made determination by the column elution method impractical due to the extremely large reservoir volume which would be required to facilitate multiple samples to be taken. Therefore the flask method was used as this allowed for larger sample volumes to be taken for analysis.
The concentration (g/L) of test item in the sample solutions is shown in the following table:
Sample Number | Time Shaken at ~ 30 °C (hours) | Time Equilibrated at 20 °C (hours) | Concentration (g/L) | Solution pH |
1A 1B | 24 | 24 | < 5.06 X 10-5 | 6.75 |
< 5.06 X 10-5 | ||||
2A 2B | 48 | 24 | < 5.06 X 10-5 | 5.91 |
< 5.06 X 10-5 | ||||
3A 3B | 72 | 24 | < 5.06 X 10-5 | 6.35 |
< 5.06 X 10-5 |
Description of key information
Key Study:
In an OECD 105 study, conducted according to GLP, the water solubility of the test material is less than 0.0506 mg/L, and is therefore considered insoluble in water.
Key value for chemical safety assessment
- Water solubility:
- 0.051 mg/L
- at the temperature of:
- 20 °C
Additional information
Supporting Studies:
In an EU Method A.6 study, not conducted according to GLP, the water solubility of the structurally similar read across substance is less than 0.01 mg/L.
In an EU Method A.6 study, not conducted according to GLP, the water solubility of the structurally similar read across substance is less than 0.05 mg/L.
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